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Michelle Perez, Senior Associate for SWCS Lombard, IL, July 29, 2014
IMPROVING WATER
QUALITY
A National Modeling Analysis on Increasing Cost
Effectiveness through Better Targeting of U.S. Farm
Conservation Funds
IMPROVING WATER QUALITY
THROUGH BETTER TARGETING
wri.org/water/water-quality-targeting
July 28, 2014 MRBI Presentation at SWCS 
July 29, 2014 National Analysis Presentation at SWCS 
RESEARCH QUESTIONS
1. How cost effective is the current (BAU) approach?
– BAU=spending on nutrient & erosion control practices: ’06-’11
2. How much more effective could it be with targeting?
– 3 targeting approaches
3. How do results change depending on what
environmental benefit is being optimized?
– N, P, & sediment reduction & soil C sequestration
4. If programs were designed to achieve the most cost-
effective benefits, where would the funds be spent?
DEFINING TARGETING
• Geographic targeting –
Prioritizing areas:
a. Greatest environmental
impairments
b. Pristine conditions
c. Greatest change in
environmental conditions
possible
• Benefit-cost targeting –
Identifying acres and
practices that can produce
the most environmental
benefits per dollar spent
(e.g., most pounds of N
reductions/$)
DATA & MODELS
• Farmer survey data
from Natural Resources
Inventory-Conservation
Effects Assessment
Project (NRI-CEAP)
• Agricultural Policy
Extender (APEX) model
• Economic optimization
model
MODELING LIMITATIONS
• Geographic targeting -
Prioritizing areas with
greatest change possible
• Model analysis is at edge-
of-field
• Doesn’t account for where
acres are vis a vis impaired
water bodies
• Prioritizes acres that offer
the biggest edge-of-field
pollution reduction
opportunities
201 4-DIGIT WATERSHEDS
& ESTIMATING BAU COST EFFECTIVENESS
BAU $ spent in 
each watershed
on average
# lbs. N reduced 
at edge‐field in 
each watershed
$/# lbs. N reduced = level 
of cost effectiveness in 
each watershed 
3 TARGETING APPROACHES IN MODEL
DUAL TARGETING MORE EFFECTIVE THAN BAU
12 x
8 x
8 x
7.5 x
DUAL TARGETING IS MOST COST EFFECTIVE
• Geographic + benefit-cost targeting could
result in 7 to 12 times more environmental
benefits per dollar spent than BAU
• Benefit-cost targeting alone could achieve 4 to
9 times the benefits as BAU
• Geographic targeting alone could be better or
worse than BAU
CHOOSING WHAT TO TARGET
• Optimizing for
multiple benefits
(N, P, & soil C) yields
more co-benefits &
fewer trade-offs than
optimizing for
individual benefits
• If only 1 benefit can
be targeted,
optimizing for
phosphorus
reductions is best
TARGETING MAY MEAN MORE ACRES
16.8
12.8
8.7
Benefit‐Cost
Targeting for
Sediment
Dual Targeting for
Nitrogen
BAU
1.5 times 
more acres
(Millions of acres)
BUSINESS-AS-USUAL ALLOCATION OF FUNDS
FUNDING ALLOCATIONS FOR
MULTIPLE BENEFITS OPTIMIZATION (N, P, C)
FUNDING ALLOCATIONS FOR
PHOSPHORUS OPTIMIZATION
FUNDING ALLOCATIONS FOR
NITROGEN OPTIMIZATION
FUNDING ALLOCATIONS FOR
SEDIMENT OPTIMIZATION
FUNDING ALLOCATIONS FOR
SOIL CARBON OPTIMIZATION
WHAT THIS STUDY IS & IS NOT
• Not an analysis of what NRCS could have
done in past due to
– Scientific & technical barriers
– Institutional & implementation barriers
– Social & political barriers
• Is an analysis of what NRCS could be
doing in the future
RECOMMENDATIONS
1. Track environmental benefits
2. Rank applications according to
benefit-cost ratios
3. Conduct pilot projects
4. Improve state funding allocation
formulas
Thank You!
Michelle Perez, PhD
202-729-7908
mperez@wri.org

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Increasing cost effectiveness of conservation programs

  • 1. Michelle Perez, Senior Associate for SWCS Lombard, IL, July 29, 2014 IMPROVING WATER QUALITY A National Modeling Analysis on Increasing Cost Effectiveness through Better Targeting of U.S. Farm Conservation Funds
  • 2. IMPROVING WATER QUALITY THROUGH BETTER TARGETING wri.org/water/water-quality-targeting July 28, 2014 MRBI Presentation at SWCS  July 29, 2014 National Analysis Presentation at SWCS 
  • 3. RESEARCH QUESTIONS 1. How cost effective is the current (BAU) approach? – BAU=spending on nutrient & erosion control practices: ’06-’11 2. How much more effective could it be with targeting? – 3 targeting approaches 3. How do results change depending on what environmental benefit is being optimized? – N, P, & sediment reduction & soil C sequestration 4. If programs were designed to achieve the most cost- effective benefits, where would the funds be spent?
  • 4. DEFINING TARGETING • Geographic targeting – Prioritizing areas: a. Greatest environmental impairments b. Pristine conditions c. Greatest change in environmental conditions possible • Benefit-cost targeting – Identifying acres and practices that can produce the most environmental benefits per dollar spent (e.g., most pounds of N reductions/$)
  • 5. DATA & MODELS • Farmer survey data from Natural Resources Inventory-Conservation Effects Assessment Project (NRI-CEAP) • Agricultural Policy Extender (APEX) model • Economic optimization model
  • 6. MODELING LIMITATIONS • Geographic targeting - Prioritizing areas with greatest change possible • Model analysis is at edge- of-field • Doesn’t account for where acres are vis a vis impaired water bodies • Prioritizes acres that offer the biggest edge-of-field pollution reduction opportunities
  • 7. 201 4-DIGIT WATERSHEDS & ESTIMATING BAU COST EFFECTIVENESS BAU $ spent in  each watershed on average # lbs. N reduced  at edge‐field in  each watershed $/# lbs. N reduced = level  of cost effectiveness in  each watershed 
  • 9. DUAL TARGETING MORE EFFECTIVE THAN BAU 12 x 8 x 8 x 7.5 x
  • 10. DUAL TARGETING IS MOST COST EFFECTIVE • Geographic + benefit-cost targeting could result in 7 to 12 times more environmental benefits per dollar spent than BAU • Benefit-cost targeting alone could achieve 4 to 9 times the benefits as BAU • Geographic targeting alone could be better or worse than BAU
  • 11. CHOOSING WHAT TO TARGET • Optimizing for multiple benefits (N, P, & soil C) yields more co-benefits & fewer trade-offs than optimizing for individual benefits • If only 1 benefit can be targeted, optimizing for phosphorus reductions is best
  • 12. TARGETING MAY MEAN MORE ACRES 16.8 12.8 8.7 Benefit‐Cost Targeting for Sediment Dual Targeting for Nitrogen BAU 1.5 times  more acres (Millions of acres)
  • 14. FUNDING ALLOCATIONS FOR MULTIPLE BENEFITS OPTIMIZATION (N, P, C)
  • 18. FUNDING ALLOCATIONS FOR SOIL CARBON OPTIMIZATION
  • 19. WHAT THIS STUDY IS & IS NOT • Not an analysis of what NRCS could have done in past due to – Scientific & technical barriers – Institutional & implementation barriers – Social & political barriers • Is an analysis of what NRCS could be doing in the future
  • 20. RECOMMENDATIONS 1. Track environmental benefits 2. Rank applications according to benefit-cost ratios 3. Conduct pilot projects 4. Improve state funding allocation formulas
  • 21. Thank You! Michelle Perez, PhD 202-729-7908 mperez@wri.org